Suzie and her mom, Joy, collecting western redbud (Cercis occidentalis) seeds a couple weeks ago.
The summer seed collection season will be winding down over the next couple months as we shift into cooler, moister fall weather. This time of year we are usually too busy with seed collecting and cleaning to do much blog writing, but we wanted to share some highlights from this spring and summer before the summer slips away.
On May 23rdSuzie Savoie of Klamath-Siskiyou Native Seeds gave a presentation, Food Plants for Butterflies Part 2, for Pollinator Project Rogue Valley. This presentation highlights native plants that are beneficial for butterflies in southwest Oregon and northwest California. You can watch the Zoom presentation below to learn more about native plants that butterflies love!
On June 1st, Suzie gave a presentation, Growing Native Plants from Seed, for the Jackson County Master Gardeners Association at the OSU Extension meeting room in Central Point in southern Oregon. This in-person presentation covered the basics of growing native plants from seed using simple techniques for the native home nursery.
On June 17th Suzie and Luke gave a tour of the Troon Vineyard Native Plant and Pollinator Botanical Garden, at Troon Vineyard in the Applegate Valley in southern Oregon. Suzie and Luke from Klamath-Siskiyou Native Seeds helped create the project and are really pleased to share the abundance of blooms, butterflies and bees in the native garden! Below are some photos of the tour and videos of the pollinator profusion on a couple species of wildflower growing in the gardens: coyote mint and arrowleaf buckwheat!
On July 1stSuzie led the first of a two-part workshop on private, conserved land below Mt. Ashland in southern Oregon, where participants were able to tour Klamath-Siskiyou Native Seed’s seven year old native seeding project on the property, and learn about how it was established. Workshop participants learned to identify different species, as well as the specific growing requirements to grow them from seed. Participants also learned to identify and pull non-native plants that have seeded into the gardens, and some time was spent pulling weeds and talking about weed management and overall site maintenance. You can view the photos from Part 1 of the workshop at PPRV’s photo album from the day at the following link:
Part 2 of the workshop is coming up this coming weekend, and will be focused on seed collection, seed cleaning, seed sowing, and more hands-on activities. We’re looking forward to it!
On July 14-16 Klamath-Siskiyou Native Seeds (KSNS) sponsored the Siskiyou Crest Festival, organized by the Siskiyou Crest Coalition, that took place in Williams in southern Oregon. We were one of many businesses, non-profits, and individuals that chipped in to make the event a success! The event featured a series of field trips, speakers, poetry, an art show, and so much more! Luke from KSNS was part of a keynote speaker lineup at the event, with his presentation, The Siskiyou Crest: Relationships, Biodiversity & Connectivity. And Luke and Suzie led one of the free field trips on July 14th, as part of the Festival, up to Lily Pad Lake in the Red Buttes Wilderness.
Lily Pad Lake field trip in the Red Buttes, led by Luke Ruediger and Suzie Savoie as part of the Siskiyou Crest Festival.Luke Ruediger, keynote panel for the Siskiyou Crest Festival
And of course we continue to be out and about and in the field as much as possible collecting seeds to bring you the species you want to grow! Every year is different, with some species producing seed more than others, but every year we add new species to our offerings, and this year is no different. We’ve recently added the following new, late blooming wildflower species to our SHOP page:
After giving this presentation in person for the past two years at various events in southwest Oregon, Suzie recorded it on Zoom for folks to watch on video from the comfort of their own homes. Now that spring has arrived and wildflowers are blooming across the region, it’s time to grow our shared appreciation for the botanical biodiversity of the Siskiyou Mountains! Many of the species covered in this presentation are still buried under feet of snow from this winter’s amazing snowpack, so start dreaming of seeing these flowers this summer! In the meantime, this presentation does cover species from low and mid elevations as well, so check it out and get out and enjoy the flowers this spring and summer!
The McKinney Fire burned a portion of wooden fence and irrigation in one area of the native planting project at KRC.
As winter weather draws us indoors this time of year, it gives us time to reflect on some important experiences and learning opportunities in 2022, including this summer’s McKinney Fire, which tested the fire resiliency of our native planting and seeding projects at Klamath River Club on the Klamath River in northern California.
This summer one of Klamath-Siskiyou Native Seeds’ long-term native seeding and planting projects interacted with the McKinney Fire on the Klamath River in northern California, and it made it out pretty good, showing that growing native plants for the benefit of pollinators, wildlife, birds and native plant conservation can be an integral part of hardening your home and creating a fire resilient landscape on your property.
Wildfire is an elemental part of the ecological landscape of the Klamath-Siskiyou region, and it interacts with and impacts human communities in many different ways. The lives of most everyone who lives in the Klamath-Siskiyou region are touched in some way by wildfire, and will continue to be.
KRC structures with native plant landscaping made it through the McKinney Fire. You can see the visible fire effects from the McKinney Fire on the slopes above KRC. The fire moved through the property with no one there to fight the fire, but many structures and most of the native plantings and seeded areas remained unburned.
In many ways, the work we do at Klamath-Siskiyou Native Seeds is dependent on wildfire, as many of the species that we collect seed of and supply seed for are invigorated and nourished by wildfire, and some are truly dependent on wildfire for their survival and regeneration. We also do a lot of our seed collection in the post-fire environment, usually 2-3 years after it burns, as that is when herbaceous plants have put on extraordinary growth and flowers in the post-fire environment, making the access to an abundance of seed much easier to locate.
May 2022August 2022KRC river access area deck overlooking the Klamath River before and after the McKinney Fire.
Where we live and work at the base of the Siskiyou Crest near the Red Buttes Wilderness, has experienced many wildfires in the last 20 years, including the 38,000-acre Abney Fire that burned in 2017 in our canyon for two months, creeping around mainly in the understory and replenishing the forests, woodlands and meadows with a long suppressed natural process.
Our family is lucky enough to have experienced low-intensity, understory wildfire next to our home with little threat to our structures or safety; however, our family has also experienced the devastating loss of a home to wildfire when Luke’s Mom’s home burned in the fast-moving, wind-driven Almeda Fire in Talent, Oregon in 2020. This fire destroyed 2,300 homes and killed three people. Luke’s mom will always live with the trauma and grief of losing so much so quickly, including sentimental and historic items that meant so much to her.
Photos from KRC showing some McKinney Fire burned areas in the foreground within or near the native seeding and planting project areas, as well as the fire effects on the slope above.
Klamath River Club is located along the Klamath River near the town of Klamath River, and at the northern edge of the McKinney Fire footprint, in between the fire and the northern spot fire that occurred north of the river that was discontinuous with the main body of the fire.
Yet, after many years of working on habitat restoration and native seeding and planting projects, for the first time, one of our project areas was tested by wildfire this past summer on the Klamath River. Our lives and work were again touched by wildfire, but in a different way this time. One of our long-term native seeding and planting projects at the private fishing retreat, Klamath River Club (KRC) on the Klamath River was partially burned in the 66,000-acre McKinney Fire.
The McKinney Fire was a dramatic semi-natural event, ignited by downed powerlines, burning through significant private industrial timber lands and fueled by explosive fire behavior, strong winds, collapsing pyrocumulus plumes and sudden, extreme rain events. The McKinney Fire tragically killed four people and destroyed at least 185 structures, including most of the town of Klamath River, California.
Started by sparking Pacific Power power lines, the fire quickly roared to life during an unprecedented heat wave and wind event. According to temperature gauges at KRC, the area experienced a record temperature of 116 the day the fire started, and in less than 24 hours the fire roared through the small settlement of Klamath River, burning many homes, trailer parks, the Klamath River Community Hall, a building that housed archives for the Karuk Tribe and the post office. When it reached KRC no one was there, not even fire crews, as they were busy with emergency evacuations, trying to save lives and get people out of the fire area. Crews were also focused on implementing structural protection along Hwy 96 with limited resources and under dangerous conditions, attempting to protect homes at the heart of the small hamlet of Klamath River. The McKinney Fire moved through the KRC property for an estimated 12 hours with no one there, and burned without the influence of fire suppression activities, showing how the fire naturally interacted with the human infrastructure, native plant gardens and habitat restoration projects.
Some silver bush lupine (Lupinus albifrons) and a portion of a native hedgerow burned in this area of KRC where native planting and seeding had taken place. As you can see though, the fire stopped spreading on its own and didn’t burn the entire area.
Thankfully KRC was developed with wildfire in mind, as owners Tom and Annette had previously lost a home to wildfire during the Oakland Firestorm of 1991 in Oakland, California, a deadly and devastating fire that killed 25 people and burned 2,843 single-family dwellings and 437 apartment and condominium units. Because of this past experience, Tom and Annette helped residents impacted by the Almeda Fire by gathering donated items from people in Oakland, California to help those who lost their homes during the Almeda Fire in the Rogue Valley years later. These experiences also helped inform the management choices they made at KRC while developing the human infrastructure, landscaping and defensible space around the property.
As part of the habitat restoration work at KRC, the first project was blackberry removal, followed by riparian tree and shrub planting along the river. This took place in between the river and structures, starting in 2017. This early decision to implement invasive blackberry removal along the river corridor adjacent to the developed portions of the property, and the emphasis on native riparian plants, was probably the most important factor that contributed to KRC surviving the McKinney Fire with only some losses. Blackberry removal and maintenance has continued at KRC near the homes and structures every year since 2017, keeping blackberry growth to a minimum and reducing fuels less than 100′ from structures and human infrastructure on the property.
Invasive blackberry made this area along the Klamath River burn hot on the upstream part of the KRC property.One wall tent burned, and another survived during the McKinney Fire at KRC on the downstream part of the property.
Along the Klamath River in this portion of KRC extensive blackberry removal had taken place. As you can see, none of the riparian vegetation burned in this location, protecting the tiny house and native oak trees from burning.
As you can see in these photos, areas along the river that were still colonized with dense thickets of blackberries burned completely to the ground. Yet, where blackberry had been removed, the native riparian vegetation was largely unscathed and the reduction in fire intensity likely led to a decrease in residual heat and ember shower effecting the adjacent structures. The gray willow that dominates the Klamath River corridor, and native willow in general, is very fire resilient and is stimulated by wildfire, so it burning in and of itself is not problematic; however, it burning near structures and sending up embers that can help ignite nearby infrastructure does make a difference. So, in this scenario, removing the invasive blackberry and encouraging native trees and shrubs made the structures at KRC more fire resilient, reduced fire activity on the property and reduced the severity of the fire. It also essentially stopped the fire and may have saved much of the human infrastructure at KRC.
Invasive Himalayan blackberries had not been removed from this part of the river vegetation, and the area burned hot as the blackberries burned, burning most of the gray/coyote willow, but thankfully only one of the canvas wall tents burned in this area.
In all, the main structure, the bathhouse, a large outdoor kitchen/pavilion area, multiple large canvas wall tents on platforms, the pump house, the outdoor shower, and the garage structure all made it out just fine as the fire moved through the property. Some losses included two metal containers used for tool storage where the entire contents burned. The metal structures concentrated heat and baked the contents from the inside out. Although the metal containers did not burn, their contents were incinerated. Additionally, two canvas wall tents on platforms, and a woodshed with four cords of wood were burned. Compared to many who lost everything in the McKinney Fire, KRC made it out pretty good, with much to be thankful for.
The McKinney Fire arrived at Klamath River Club at 10:22 am on the morning of July 30th, on the second day of the fire. You can see the flames approaching from downstream.
The day the fire started Tom and Annette watched the fire burn remotely from their security cameras. The images were devastating that night as the dark images showed fire moving through the property and flames burning in different areas. As they went to bed that night, they thought KRC was going to be a total loss, but the morning daylight revealed that much of KRC made it through the fire, and some of the impressive flames and images from the night before was the firewood shed on fire, making it appear much worse than it actually was.
When Tom was finally able to return to KRC and visit the property with CALFIRE staff, they told him that the work he had done to create defensible space using native plants and removing blackberries had helped save the structures at KRC. Klamath-Siskiyou Native Seeds had done a lot of this work, and we are proud to have helped KRC be more fire resilient during the McKinney Fire.
The McKinney Fire burning through Klamath River Club at 8:31pm and 10:00pm on the evening of July 30th. The morning of July 31st, after the McKinney Fire moved through Klamath River Club.
As the McKinney Fire moved through the property it partially burned some of the native plantings, but most of the areas that we had planted and seeded remained completely unburned. As mentioned earlier, areas along the river treated to remove invasive blackberries stayed lush and green with primarily native gray willow (Salix exigua), but also some Oregon ash (Fraxinus latifolia), white alder (Alnus rhombifolia), incense-cedar (Calocedrus decurrens), white oak (Quercus garryana) and black oak (Quercus kelloggii) survived the fire. In the understory of these larger, established plants grow smaller native plantings, including a mixture of native trees and shrubs, that were also unscathed during the McKinney Fire.
A newly planted native hedgerow partially burned, but many plants survived.Western thistle (Cirsium occidentale) burned in the seeded native meadow.Klamath plum (Prunus subcordata) burned on the edge of the native plant garden.
Along the road going through KRC some metal containers that stored tools were burned and removed from the site already at the time of this photo. You can see the established native hedgerow made it out fine, along with the pump house and tiny house.
There are a lot of factors that determine the intensity of a wildfire, and whether or not structures or vegetation will burn, but one of the major factors near homes is wind and ember shower. Thankfully all the structures at KRC have metal roofs which help prevent ember ignition. Embers did ignite a few places in the native plantings at KRC during the McKinney Fire, but they mostly just smoldered around in the bark mulch and burned up some of the plantings in a few areas. Probably less than 5% of the areas planted and seeded with native plants burned, and only a small fraction of that was negatively impacted. Well established plants sprouted back really quickly after the fire; whereas, some shrubs and perennials that were not well established, and were only planted a year or two ago, didn’t come back after being burned.
Being resilient to the fire allowed the native gardens and habitat at KRC to act as an oasis in an area which burned pretty hot overall in the McKinney Fire, providing valuable pollen and nectar for endangered monarch butterflies and other pollinators and wildlife within the fire footprint. Monarch butterflies used the milkweed in the native plant gardens at KRC throughout the summer and early fall at KRC, nectaring on the flowers, laying eggs on the plants, caterpillars munching on the leaves, caterpillars eclosing from chrysalises on the plants, and producing more monarchs and that will help the imperiled western monarch butterfly population.
Monarch butterfly caterpillars using the showy milkweed (Asclepias speciosa) that is very abundant in the KRC native plant gardens. The gardens primarily didn’t burn during the fire, so abundant milkweed remained for monarchs to use in the post McKinney Fire environment.
Additionally, naturally occurring showy milkweed on the property that burned in the fire was growing back and pushing new growth within weeks of the fire.
Showy milkweed (Asclepias speciosa) resprouting at KRC on August 23, 2022, just 23 days after the McKinney Fire moved through the area.
Overall, the impacts to human infrastructure and native plantings at KRC were minimal, showing that native plantings, the removal on non-native species and the maintenance of defensible space had a positive effect on the overall impact of the McKinney Fire at KRC. .
The plants that didn’t make it through the fire were replanted this fall and efforts at KRC will continue focusing on native plant restoration, native plant gardening, defensible space and home hardening that will beautify the property, provide valuable pollinator and wildlife habitat, and help KRC weather the next fire storm. Living with wildfire takes preparation and thoughtful management of your surroundings, it also requires a little luck. KRC was both lucky and prepared, allowing the property to continue thriving with wildfire on the Klamath River. Fire is an inevitable part of life, but losing homes, structures and infrastructure is not inevitable if we work to adequately prepare homes and communities with defensible space and home hardening.
One wall tent that burned and one wall tent that survived at KRC.Burned wall tent and fire mosaic.Native mugwort sprouted back right away along the Klamath River at KRC.
The McKinney Fire burned along the Klamath River in this photo (on left), but stopped itself at the path and even with ember showers, didn’t burn the native seeded meadow in the foreground of this pine tree. Even though one of the canvas wall tents behind the tree did burn, another in the distance didn’t burn.
For more information please check out the following:
(Click on the title to view and download the chart in Excel format.)
It can be difficult to find information regarding seed germination for native plant species. Through our own native plant propagation and growing experience, as well as long-term seed germination experimentation, we have developed a seed germination chart for species we often have in our inventory. This chart specifies the pretreatment needs for seed through cold-moist stratification (chilling requirements) or heat treatment, for natural or artificial seed germination, as well as recommendations for planting seed outside for natural seed germination. Germination rates can vary so your own personal experimentation is encouraged!
Common Name
Botanical Name
Seed Germination Instructions
Vine maple
Acer circinatum
30-60 days warm-moist stratification followed by 90-120 days cold-moist stratification. Sow outside in fall.
Common yarrow
Achillea millefolium
No pretreatment required. Sow in fall or spring on or just below the soil surface. Needs warm soil and light to germinate.
Vanillaleaf
Achlys triphylla
60 days cold-moist stratification. Sow outside in fall to late winter.
Columbia monkshood
Aconitum columbianum
60 days cold-moist stratification. Sow outside in fall to late winter.
Horse mint
Agastache urticifolia
30-60 days cold-moist stratification. Sow outside in fall to late winter.
Western joepiweed
Ageratina occidentalis
No pretreatment required. Sow outside in fall to early spring. Germination may be improved with 30 days cold stratification
California dandelion
Agoseris grandiflora
No pretreatment required. Sow outside in fall to early spring. Germination may be improved with 30 days cold stratification.
Tapertip onion
Allium acuminatum
30-60 days cold-moist stratification. Sow outside in fall to late winter.
Pacific mountain onion
Allium validum
60-90 days cold-moist stratification. Sow outside in fall to late winter.
Menzies’ fiddleneck
Amsinckia menziesii
60 days cold-moist stratification. Sow outside in fall for best germination.
Sharptooth angelica
Angelica arguta
60 days cold-moist stratification. Sow outside in fall to late winter.
Woodland madia
Ansiocarpus madioides
30-60 days cold-moist stratification. Sow outside in fall to late winter.
Western columbine
Aquilegia formosa
60 days cold-moist stratification. Sow outside in fall to late winter.
California spikenard
Aralia californica
90-120 days cold-moist stratification. Sow outside in fall for best germination.
Goat’s beard
Aruncus dioicus
30-60 days cold-moist stratification. Sow outside in fall to late winter. Plant on soil surface or lightly cover. Seed needs light to germinate.
Heartleaf milkweed
Asclepias cordifolia
60 days cold-moist stratification. Sow outside in fall to early spring.
Narrowleaf milkweed
Asclepias fascicularis
60 days cold-moist stratification. Sow outside in fall to early spring.
Showy milkweed
Asclepias speciosa
60 days cold-moist stratification. Sow outside in fall to early spring.
California harebell
Asyneuma prenanthoides
60 days cold-moist stratification. Sow in fall to late winter. Sow on soil surface or lightly cover. Seed needs light to germinate.
Deltoid balsamroot
Balsamorhiza deltoidea
90 days cold-moist stratification. Sow outside in fall.
Tall Oregon grape
Berberis (Mahonia) aquifolium
90 days cold-moist stratification. Sow outside in fall to late winter.
Cascade Oregon grape
Berberis (Mahonia) nervosa
60 days cold-moist stratification. Sow in fall to late winter.
California brome
Bromus carinatus
No pretreatment required. Sow outside in fall to early spring.
Chinook brome
Bromus laevipes
No pretreatment required. Sow outside in fall.
Tolmie’s cats ear
Calochortus tolmiei
30-60 days cold-moist stratification. Sow in fall to late winter.
Marsh marigold
Caltha leptosepala
60-90 days cold-moist stratification. Sow in fall to late winter.
Large camas
Camassia leichtlinii
60-90 days cold-moist stratification. Sow in fall to late winter.
Deer brush
Ceanothus integerrimus
Soak in hot (not boiling) water for 24 hours, then 60-90 days cold-moist stratification. Sow outside in fall to late winter.
Birch leaf mountain mahogany
Cercocarpus betuloides
60 days cold-moist stratification. Sow outside in fall to late winter.
Soaproot
Chlorogalum pomeridianum
No pretreatment required. Sow outside in fall to early spring.
Fireweed
Chamerion angustifolia
60 days cold-moist stratification. Sow outside in fall to late winter.
Western redbud
Cercis occidentalis
Soak in hot (not boiling) water for 24 hours, then 60-90 days cold-moist stratification. Sow outside in fall to late winter.
Western clematis
Clematis ligusticifolia
30-60 days cold-moist stratification. Sow outside in fall to late winter.
Hound’s tongue
Cynoglossum grande
30-60 days cold-moist stratification. Sow outside in fall to late winter.
Mountain larkspur
Delphinium glaucum
90-120 days cold-moist stratification. Sow outside in fall.
Meadow larkspur
Delphinium nuttallianum
90-120 days cold-moist stratification. Sow outside in fall.
Henderson’s shooting star
Dodecatheon hendersonii
60-90 days cold-moist stratification. Sow outside in fall to late winter.
Squirreltail grass
Elymus elymoides
No pretreatment required. Sow outside in fall to early spring.
Blue wildrye
Elymus glaucus
No pretreatment required. Sow outside in fall to early spring.
Capitate sandwort
Eremogone congesta
60-90 days cold-moist stratification. Sow outside in fall to late winter.
Tall wooly buckwheat
Eriogonum elatum
60 days cold-moist stratification. Sow outside in fall to late winter.
Arrowleaf buckwheat
Eriogonum compositum
60 days cold-moist stratification. Sow outside in fall to late winter.
Barestem buckwheat
Eriogonum nudum
60 days cold-moist stratification. Sow outside in fall to late winter.
Sulphur flower buckwheat
Eriogonum umbellatum
60 days cold-moist stratification. Sow outside in fall to late winter.
Oregon sunshine
Eriophyllum lanatum
30 days cold-moist stratification. Sow outside in fall to late winter.
Henderson’s fawn lily
Erythronium hendersonii
90 days cold-moist stratification. Sow outside in fall.
Scarlet monkey flower
Erythranthe (Mimulus) cardinalis
No pretreatment required. Sow outside in fall to early spring. Seeds need light to germinate, surface sow.
Yellow seep monkey flower
Erythranthe (Mimulus) guttata
No pretreatment required. Sow outside in fall to early spring. Seeds need light to germinate, surface sow.
California poppy
Eschscholzia californica
30 days cold-moist stratification. Sow outside in fall or early spring.
Western goldentop
Euthamia occidentalis
No pretreatment required. Sow outside in fall to early spring.
California fescue
Festuca californica
30 days cold-moist stratification. Sow outside in fall or early spring.
Roemer’s fescue
Festuca roemeri
30 days cold-moist stratification. Sow outside in fall or early spring.
Cascara
Frangula purshiana
60-90 days cold-moist stratification. Sow in fall to late winter.
Bluehead gilia
Gilia capitata
30 days cold-moist stratification. Sow outside in fall.
White rushlily
Hastingsia alba
60-90 days cold-moist stratification. Sow outside in fall to late winter.
Bigelow’s sneezweed
Helenium bigelovii
30 days cold-moist stratification. Sow outside in fall to late winter.
Cowparsnip
Heracleum maximum
120 days cold-moist stratification. Sow outside in fall.
Alum root
Heuchera micrantha
60 days cold-moist stratification. Sow outside in fall. Seeds need light to germinate, surface sow.
Oceanspray
Holodiscus discolor
90-120 days cold-moist stratification. Sow outside in fall.
Broad leaved lotus
Hosackia crassifolia
Soak in hot (not boiling) water for 24 hours, then 60-90 days cold-moist stratification. Sow in fall to late winter.
Scarlet gilia
Ipomopsis aggregata
30 days cold-moist stratification. Sow outside in fall to early spring.
Red beardtongue
Keckiella corymbosa
30 days cold-moist stratification. Sow outside in fall or early spring.
Bush beardtongue
Keckiella lemmonii
30 days cold-moist stratification. Sow outside in fall or early spring.
Bolander’s tarweed
Kyhosia bolanderi
30-60 days cold-moist stratification. Sow outside in fall to late winter.
Siskiyou lewisia
Lewisia cotyledon
30-60 days cold-moist stratification. Sow outside in fall to late winter.
Blue wild flax
Linum lewisii
30 days cold-moist stratification. Sow outside in fall or early spring.
California lomatium
Lomatium californicum
60 days cold-moist stratification. Sow outside in fall to late winter.
Fernleaf biscuitroot
Lomatium dissectum
60 days cold-moist stratification. Sow outside in fall.
Bigseed biscuitroot
Lomatium macrocarpum
60 days cold-moist stratification. Sow outside in fall to late winter.
Nineleaf buscuitroot
Lomatium triternatum
60 days cold-moist stratification. Sow outside in fall to late winter.
Common lomatium
Lomatium utriculatum
60 days cold-moist stratification. Sow outside in fall to late winter.
Pink honeysuckle
Lonicera hispidula
60-90 days cold-moist stratification. Sow outside in fall.
Sickelkeel lupine
Lupinus albicaulis
Soak in hot (not boiling) water for 24 hours, then 30 days cold-moist stratification. Sow outside in fall to early spring.
Silver bush lupine
Lupinus albifrons
No pretreatment required. Sow outside in fall to early spring.
Velvet lupine
Lupinus leucophyllus
Soak in hot (not boiling) water for 24 hours, then 30 days cold-moist stratification. Sow outside in fall to early spring.
Elegant tarweed
Madia elegans
No pretreatment required. Sow outside in fall to early spring.
Large false Soloman’s seal
Maianthemum racemosum
Seed takes two years to germinate. Sow outside in fall. 6 months cold-moist stratification, followed by 4 months warm-moist stratification, followed by another 5 months cold-moist stratification.
Giant blazingstar
Mentzelia laevicaulis
60-90 days cold-moist stratification. Sow outside in fall.
Coyote mint
Monardella odoratissima
30 days cold-moist stratification. Sow outside in fall to late winter.
Coyote tobacco
Nicotiana attenuata
No pretreatment required. Sow outside, or start in a greenhouse in spring.
Indian tobacco
Nicotiana quadrivalvis
No pretreatment required. Sow outside, or start in a greenhouse in spring.
False turtlehead
Nothochelone nemorosa
60-90 days cold-moist stratification. Sow outside in fall.
Douglas’ grasswidow
Olsynium douglasii
90-120 days cold-moist stratification. Sow outside in fall.
Siskiyou Mountains owl’s clover
Orthocarpus cuspidatus
90 days cold-moist stratification. Sow outside in fall.
Indian warrior
Pedicularis densiflora
30 days cold-moist stratification. Sow in fall. Hemiparasite, needs host plant to thrive. Parasitic on members of the heath family, such as manzanita or madrone.
Siskiyou penstemon
Penstemon anguineus
60-90 days cold-moist stratification. Sow outside in fall to late winter.
Hot rock penstemon
Penstemon deustus
60-90 days cold-moist stratification. Sow outside in fall to late winter.
Mountain blue penstemon
Penstemon laetus
60-90 days cold-moist stratification. Sow outside in fall to late winter.
Small flowered penstemon
Penstemon procerus
60-90 days cold-moist stratification. Sow outside in fall to late winter.
Western sweet coltsfoot
Petasites frigidus
No pretreatment required. Sow outside in fall to early spring.
Varilieaf phacelia
Phacelia heterophylla
30 days cold-moist stratification. Sow outside in fall or early spring. Seeds need light to germinate, surface sow.
Tall phacelia
Phacelia procera
30 days cold-moist stratification. Sow outside in fall. Seeds need light to germinate, surface sow.
Mock orange
Philadelphus lewisii
90-120 days cold-moist stratification. Sow outside in fall.
Pacific ninebark
Physocarpus capitatus
30 days cold-moist stratification. Sow outside in fall or early spring.
Hooker’s fairybells
Prosartes hookeri
60-90 days cold-moist stratification. Sow outside in fall.
Chokecherry
Prunus virginiana
90-120 days cold-moist stratification. Sow outside in fall.
Bitter cherry
Prunus emarginata
90-120 days cold-moist stratification. Sow outside in fall.
Golden currant
Ribes aureum
90 days cold-moist stratification. Sow outside in fall.
Wax currant
Ribes cereum
90-120 days cold-moist stratification. Sow outside in fall.
Sierra gooseberry
Ribes roezlii
90-120 days cold-moist stratification. Sow outside in fall.
Sticky currant
Ribes viscosissimum
90 days cold-moist stratification. Sow outside in fall.
Thimbleberry
Rubus parviflorus
30 days cold-moist stratification. Sow outside in fall or early spring.
Waxy coneflower
Rudbeckia glaucescens
30 days cold-moist stratification. Sow outside in fall or early spring.
Western coneflower
Rudbeckia occidentalis
30 days cold-moist stratification. Sow outside in fall or early spring.
Blue elderberry
Sambucus nigra spp. caerulea
60-90 days cold-moist stratification. Sow outside in fall.
Pacific blacksnakeroot
Sanicula crassicaulis
30-60 days cold-moist stratification. Sow outside in fall or early spring.
Lambstongue ragwort
Senecio integerrimus
30-60 days cold-moist stratification. Sow outside in fall to late winter.
Arrowleaf ragwort
Senecio triangularis
30-60 days cold-moist stratification. Sow outside in fall or early spring.
Oregon checkermallow
Sidalcea oregana
60-90 days cold-moist stratification. Sow outside in fall.
Bell catchfly
Silene campanulata
30-60 days cold-moist stratification. Sow outside in fall to late winter.
West coast Canada goldenrod
Solidago elongata
No pretreatment required. Sow outside in fall to early spring.
Western mountain ash
Sorbus scopulina
90-120 days cold-moist stratification. Sow outside in fall.
Douglas’ spiraea
Spiraea douglasii
30-60 days cold-moist stratification. Sow outside in fall to late winter.
Subalpine spiraea
Spiraea splendens
30-60 days cold-moist stratification. Sow outside in fall to late winter.
Lemmon’s needlegrass
Stipa lemmonii
90 days cold-moist stratification. Sow outside in fall.
Claspleaf twistedstalk
Streptopus amplexifolius
Seed takes two years to germinate. Sow outside in fall. 6 months cold-moist stratification, followed by 4 months warm-moist stratification, followed by another 5 months cold-moist stratification.
Leafybract aster
Symphyotrichum foliaceum
No pretreatment required. Sow outside in fall to early spring.
Fringe cups
Tellima grandiflora
30 days cold-moist stratification. Sow outside in fall or early spring.
Western false asphodel
Triantha occidentalis
60-90 days cold-moist stratification. Sow outside in fall.
Vinegarweed
Trichostema lanceolatum
60-90 days cold-moist stratification. Sow in fall to late winter.
California false hellebore
Veratrum californicum
30-60 days warm-moist stratification followed by 90-120 days cold-moist stratification. Sow outside in early fall.
Western verbena
Verbena lasiostachys
30-60 days cold-moist stratification. Sow outside in fall or early spring.
American vetch
Vicia americana
No pretreatment required. Sow outside in fall to early spring.
Narrowleaf mule’s ears
Wyethia angustifolia
90 days cold-moist stratification. Sow outside in fall.
Beargrass
Xerophyllum tenax
90-120 days cold-moist stratification. Sow outside in fall.
The tiny Siskiyou frittilaria (Frittilaria glauca). Notice the ant on the leaf.Baker cypress (Cupressus bakeri) is the most northern cypress in North America. It has a range restricted to only northern California and southern Oregon, predominately in the Klamath-Siskiyou Mountains.
Tucked into the borderlands of northern California and southern Oregon, the Klamath-Siskiyou Mountains are a place of raw, rugged beauty renowned for their biodiversity. The region is home to more species of conifer —32 of them—than any other temperate conifer forest in North America. The Klamath-Siskiyou ranks second in North America in terms of endemism (organisms found nowhere else in the world), and third in total species richness.
Shown is one of the largest Baker cypress (Cupressus bakeri) trees in the world. This grove of large trees is located at Miller Lake in the Siskiyou Mountains.
The region rises abruptly, creating a jumbled mass of rugged and diverse mountains, jagged peaks, wild rivers, and deep forest. Ancient and complex bedrock defines the Klamath-Siskiyou region as a whole. This seemingly haphazard patchwork of rock types creates and supports an unusually diverse and contrasting mosaic of habitat types, microclimates and plant diversity.
Umbrella plant or Indian rhubarb (Darmera peltatum) flower, emerging prior to the large leaves in spring.Umbrella plant or Indian rhubarb (Darmera peltatum) on Goff Creek, a tributary to the Klamath River.The following is a description of the Klamath-Siskiyou by the World Wildlife Fund. The Klamath-Siskiyou Region is on WWF’s “Global 200: The Most Outstanding and Representative Areas of Biodiversity.” For their complete description please visit the link below. This description was written in the 1990s, but is still relevant to this day.
https://www.worldwildlife.org/ecoregions/na0516“Temperate Coniferous Forest: Located in northwestern California and southwestern Oregon, complex terrain, geology, climate, and biogeographic history have created one of the Earth’s most extraordinary expressions of temperate biodiversity in the Klamath and Siskiyou Mountains. Although well known among biologists, few North Americans realize the uniqueness and importance of the species and communities in this ecoregion. Indeed, logging, mining, road building, and grazing continue to be intensive and pervasive threats to this area.
Mountain monardella (Monardella odoratissima) on Abney Butte on the Siskiyou Crest, looking toward Cook ‘n Green Butte.Horsemint (Agastache urticifolia) in the large meadows of the Silver Fork Basin, the headwaters of Elliott Creek in the Siskiyou Mountains.Description Biological Distinctiveness
The Klamath-Siskiyou ecoregion is considered a global center of biodiversity (Wallace 1982), an IUCN Area of Global Botanical Significance (1 of 7 in North America), and is proposed as a World Heritage Site and UNESCO Biosphere Reserve (Vance-Borland et al. 1995). The biodiversity of these rugged coastal mountains of northwestern California and southwestern Oregon has garnered this acclaim because the region harbors one of the four richest temperate coniferous forests in the world (along with the Southeastern Conifer forests of North America, forests of Sichuan, China, and the forests of the Primorye region of the Russian Far East), with complex biogeographic patterns, high endemism, and unusual community assemblages. A variety of factors contribute to the region’s extraordinary living wealth. The region escaped extensive glaciation during recent ice ages, providing both a refuge for numerous taxa and long periods of relatively favorable conditions for species to adapt to specialized conditions. Shifts in climate over time have helped make this ecoregion a junction and transition zone for several major biotas, namely those of the Great Basin, the Oregon Coast Range, the Cascades Range, the Sierra Nevada, the California Central Valley, and Coastal Province of Northern California. Elements from all of these zones are currently present in the ecoregion’s communities. Temperate conifer tree species richness reaches a global maximum in the Klamath-Siskiyous with 30 species, including 7 endemics, and alpha diversity (single-site) measured at 17 species within a single square mile (2.59 km2) at one locality (Vance-Borland et al. 1995). Overall, around 3,500 plant species are known from the region, with many habitat specialists (including 90 serpentine specialists) and local endemics.
Henderson’s horkelia (Horkelia hendersonii), an endemic species, on the Siskiyou Crest.
The great heterogeneity of the region’s biodiveristy is due to the area’s rugged terrain, very complex geology and soils (giving the region the name “the Klamath Knot” [A noteworthy book titled The Klamath Knot was written by David Rains Wallace in 1983]), and strong gradients in moisture decreasing away from the coast (e.g., more than300 cm (120in)/annum to less than 50 cm (20 in)/annum). Habitats are varied and range from wet coastal temperate rainforests to moist inland forests dominated by Douglas fir (Pseudotsuga menziesii), Pinus ponderosa, and P. lambertiana mixed with a variety of other conifers and hardwoods (e.g., Chamaecyparis lawsoniana, Lithocarpus densiflora, Taxus brevifolia, and Quercus chrysolepis); drier oak forests and savannas with Quercus garryana and Q. kelloggii; serpentine formations with well-developed sclerophyllous shrubs; higher elevation forests with Douglas fir, Tsuga mertensiana, Abies concolor and Abies magnifica; alpine grasslands on the higher peaks; and cranberry and pitcher plant bogs. Many species and communities have adapted to very narrow bands of environmental conditions or to very specific soils such as serpentine outcrops. Local endemism is quite pronounced with numerous species restricted to single mountains, watersheds, or even single habitat patches, tributary streambanks, or springs (e.g., herbaceous plants, salamanders, carabid beetles, land snails, see Olson 1991). Such fine-grained and complex distribution patterns means that any losses of native forests or habitats in this ecoregion can
significantly contribute to species extinction. Several of the only known localities for endemic harvestman, spiders, land snails, and other invertebrates have been heavily altered or lost through logging within the last decade, and the current status of these species is unknown (Olson 1991). Unfortunately, many invertebrate species with distribution patterns and habitat preferences that make them prone to extinction, such as old growth specialist species, are rarely recognized or listed as federal endangered species. Indeed, 83 species of Pacific Northwest freshwater mussels and land snails with extensive documentation of their endangerment were denied federal listing by the U.S. Fish and Wildlife Service in 1994 (J. Belsky, pers. comm. 1994).
Rivers and streams of the Klamath-Siskiyou region support a distinctive fish fauna, including nine species of native salmonids (salmon and trout), and several endemic or near-endemic species such as the tui chub (Gila bicolor), the Klamath small-scale sucker (Catostomus rimiculus), and the coastrange sculpin (Cottus aleuticus). Many unusual aquatic invertebrates are also occur in the region.” -WWF
Snow plant (Sarcodes sanguinea) in the Klamath Mountains.Gentner’s frittilaria (Frittilaria gentneri), an endemic species, in the foothills of the Applegate Valley.